2014 Brooks Rand Labs International Interlaboratory Comparison

2014 Brooks Applied Labs
(Formerly Brooks Rand Labs)
International Interlaboratory Comparison
Study for Arsenic Speciation in Food
Russell Gerads
Elizabeth Madonick
Michelle L. Briscoe
Tamas Ugrai
Annie Carter
Brooks Applied Labs
18804 North Creek Parkway, Suite 100
Bothell, WA 98011 USA
[email protected]
www.brooksapplied.com
January 18, 2016
Table of Contents
Introduction ..................................................................................................................................... 3
Methods........................................................................................................................................... 4
Sample Collection and Distribution ............................................................................................ 4
Data Analysis and Calculations .................................................................................................. 6
Results ............................................................................................................................................. 8
Discussion ..................................................................................................................................... 12
Participation.............................................................................................................................. 12
Performance Ratings ................................................................................................................. 14
Methods and Equipment Used .................................................................................................. 17
Future Studies ............................................................................................................................... 19
Acknowledgements ....................................................................................................................... 20
References ..................................................................................................................................... 21
Appendix A – Data Tables ............................................................................................................ 22
Introduction
The Brooks Applied Labs (formerly Brooks Rand Labs) International Interlaboratory
Comparison Study for Arsenic Speciation in Food was initiated in 2013 to provide a reliable
means for laboratories to evaluate their competency in the analysis of arsenic species in these
matrices, as well as a metric for assessing the intercomparability of data generated by different
laboratories and methods. In its second year, this study continued to be one of the largest
interlaboratory comparison studies for arsenic speciation in food conducted. This report
summarizes where the methods are successful at providing reproducible data and where more
research and method development is needed. As demonstrated by the data, this kind of
comparison study is vitally important for establishing and maintaining best practices for the
arsenic speciation analyses of food and supplements.
The 2014 study again used white rice flour as one of the study materials, but also introduced
some more complex matrices including a seasoned seaweed snack, cocoa powder, fin fish
muscle tissue (tuna), and shellfish tissue. Participants were asked to analyze the samples for
arsenic (As) species using the methods that are commonly used in their laboratory. Participants
were asked to report results for as many of the following analytes as possible, based on their
analytical methodology: total As in the sample, total As in the speciation extract, inorganic As,
and dimethylarsinic acid (DMAs). Participants were asked to measure and report the total arsenic
concentration in the sample and in their speciation extract for the purpose of determining
extraction efficiency. A sufficient number of participants reported results for monomethylarsonic
acid (MMAs) and arsenobetaine (AsB) to allow for most probable values (MPV) to be calculated
for these parameters as well. Only participants who reported at least one result for at least one
arsenic species (i.e., not just total arsenic) were included in this study report. Lab 26 did not
report any speciation results; therefore, their data was omitted from this report.
Some of the key features of the study were a broad invitation to join; a large group of
participating laboratories from around the world; anonymous data submission, analysis, and
reporting; and the inclusion of analytical method reporting. A small participation fee was
collected to cover the cost of materials and shipping to participants, and additional funding or
materials were provided by several study sponsors. Thirty laboratories from ten countries
registered to participate and were sent the study materials, and twenty-nine datasets were
received from twenty-eight different laboratories (one laboratory submitted two different datasets
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from different departments within their organization). By requesting laboratories to report
detailed information about their analytical methods, this study was again able to assess the
efficacy of specific protocols, reagents, and equipment.
Methods
Sample Collection and Distribution
Five different study materials were sourced: white rice flour, a seasoned seaweed snack, cocoa
powder, fin fish muscle tissue, and shellfish tissue. All materials were sourced and homogenized
by Brooks Rand Labs, and subsequently screened for an acceptable total As concentration of
greater than 5 parts-per-billion (ppb), or µg/kg.
Sample 1: Cocoa Powder
Cocoa powder mixed with alkalized cocoa powder was purchased commercially on-line by
Brooks Rand Labs. Each participant was sent approximately 20-25 g of sample. Screening data
indicated the total As content to be approximately 50 µg/kg and the percent moisture to be < 5%.
Sample 2: Fin Fish Tissue
The fin fish tissue was a certified reference material (CRM) for tuna fish. Dried, homogenized,
and sterilized tuna fish muscle tissue is offered as CRM BCR-627 by the Community Bureau of
Reference (BCR), the former reference materials program of the European Commission. The
certificate has been revised under responsibility of the Institute for Reference Materials and
Measurements (IRMM). Each participant was sent approximately 3 g of sample. This CRM has
certified values for total As (4800 µg/kg), DMAs (150 µg/kg), and AsB (3896 µg/kg). Screening
data indicated the percent moisture to be less than 15%.
Sample 3: Seasoned Seaweed Snack
The seasoned seaweed snack was purchased commercially on-line by Brooks Rand Labs. The
seaweed product is roasted, lightly salted, and contains corn oil, grapeseed oil, and sesame oil.
The seaweed was ground to a homogenous paste and well homogenized prior to distribution.
Each participant was sent approximately 20-25 g of sample. Screening data indicated the total As
content to be approximately 10,000 – 20,000 µg/kg and the percent moisture to be < 5%.
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Sample 4: Shellfish Tissue
Geoducks (Panopea generosa) from the Puget Sound in Washington State, USA, were donated
to Brooks Rand Labs by Taylor Shellfish Farms (Shelton, WA). Geoducks are a species of very
large, edible, saltwater clams. Upon receipt at Brooks Rand Labs, the geoducks were shucked,
frozen, and shipped to Apex Lyo, Inc. (Eugene, OR) for freeze-drying. The lyophilized tissue
was returned to Brooks Rand Labs for homogenization. Each participant was sent approximately
15 g of sample. Screening indicated the total As content to be approximately 5,000 – 10,000
µg/kg and the percent moisture to be < 10%.
Sample 5: Rice Flour
The rice flour was a standard reference material (SRM) provided by the National Institute of
Standards and Technology (NIST) – NIST SRM 1568b. The rice flour was produced from 100%
long grain river rice grown in Arkansas. Each participant was sent approximately 5 g of sample.
This CRM has certified values for total As (285 µg/kg), inorganic As (92 µg/kg), DMAs (180
µg/kg), and MMAs (11.6 µg/kg). Screening indicated the percent moisture to be < 10%.
All homogenized intercomparison study samples were placed in 20-mL borosilicate glass vials.
Vials were pre-tested and found to be from a lot that was low in total arsenic concentration. Vials
were labeled, individually double-bagged in zip-type bags, and stored in cardboard shipping
boxes.
Samples were shipped to the participating laboratories during the week of August 4, 2014.
Participating laboratories were asked to analyze samples for total arsenic and arsenic species as
previously described in accordance with their standard operating procedures, and were given no
further guidance on analytical methodology. All results were originally requested to be reported
by Tuesday, September 30, 2014, approximately 7 weeks after participants first began receiving
samples; however, based on requests from some study participants, this deadline was extended to
Sunday, October 5, 2014.
All results were reported to an independent third party, EcoChem, Inc. (Seattle, Washington,
USA), a data validation company who had no role in the study other than data management. At
EcoChem, the dataset was compiled, and a unique identifier was assigned to each laboratory,
before it was transmitted to Brooks Rand Labs. Concurrent with delivery of this report, each
participating laboratory received an e-mail containing their own unique identifier, but identifiers
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were not disclosed to any other parties, including Brooks Applied Labs. This research design
ensured there would be no bias by the preparers of this report against any participating laboratory
and that participants could submit data with the comfort of anonymity.
Data Analysis and Calculations
Each laboratory was asked to report an analytical result, detection limit, and date analyzed for
each sample and analyte. These data are the basis of the calculated most probable values (MPV)
and scores in this report. In addition, each laboratory reported information on sample
preparation, analytical methodology, and equipment. These data were used to compile
assessments of the performance of various analytical methods, but were not used in laboratory
scoring.
Due to the large number of results that were reported below the laboratories’ detection limit
(non-detects), statistical data analysis for the calculation of the MPVs for applicable
analyte/matrix combinations was performed using the Kaplan–Meier method (Ref. 1), calculated
with the Non-detects and Data Analysis (NADA) Cenfit method of the software program R (Ref.
2). This method was chosen because it more appropriately takes non-detects (data censored to
the detection limit) into account, rather than just omitting them. The Cenfit method computes an
estimate of median for censored data using the Kaplan-Meier method as the nonparametric
maximum likelihood of the MPV without assuming any specific distribution.
Statistical data analysis for the calculation of laboratory scores was performed following the
method favored by the United States Geological Society’s Standard Reference Sample Project
(Ref. 3). Data are evaluated using nonparametric statistics (Ref. 4). This statistical approach was
chosen because it is resistant to undue influence of outliers on the median.
The absolute z-value for each result is calculated using the following equations:
Z = |(X-M)|/F
and
F = Q/1.349
Where:
Z = absolute Z-value assigned to each result for the purpose of assigning a rating
X = reported value
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M = median value reported by all laboratories (excluding values below the reported
detection limit)
F = F-pseudosigma (approximates the standard deviation of traditional statistics when the
data has a Gaussian distribution); calculated by dividing the interquartile range (or
fourth-spread) by 1.349. The 1.349 value is derived from the number of standard
deviations that encompasses 50% of the data.
Q = Interquartile range (the difference between the first quartile and third quartile of a set
of data)
Participating laboratories were requested to report undetected values as being less than their
detection limit. If a value was less than that laboratory’s reported detection limit, then that value
was omitted and the “u” qualifier was added. For these samples, performance was not rated
unless the laboratory’s detection limit was less than the MPV (potential false negative) and has a
z-value greater than 2. In this case, the laboratory would receive a rating of 0 for that analyte.
In order to assign a score to each laboratory’s performance, ratings were assigned based on each
laboratory’s absolute Z-value for each analyte, as listed in Table 1.
Table 1. Descriptions of ratings assigned to each result based
on the calculated absolute Z-value.
Rating
Absolute Z-value
4 (Excellent)
3 (Good)
2 (Marginal)
1 (Poor)
0 (Unacceptable)
0.00 – 0.50
0.51 – 1.00
1.01 – 1.50
1.51 – 2.00
Greater than 2.00
Scores were not assigned if the overall number of data points (omitting values that were less than
the reported detection limit) was less than seven or when the calculated F-pseudosigma value (F)
was greater than the median value (M).
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Results
The results reported by each laboratory for each of the material types can be found in Appendix
A, along with the MPV, median value (M), mean value, F-psuedosigma (F) value, and number of
laboratories reporting results above their detection limit (n) for each parameter. If a laboratory
reported a potential false negative (result reported is less than the detection limit and the
detection limit is less than M), then the rating of “0” is highlighted in red. If the data is not
scored due to the F value being greater than the M value, then the F value is highlighted in red. If
the data is not scored because the n value is less than 7, then the n value is highlighted red.
The MPV values for each parameter are listed in Table 2. Values highlighted in red were
associated with F values that were greater than the M values; therefore, the variability in the data
was too high. In addition, datasets with less than seven results were considered too small to use
the M value as a consensus value for the purpose of scoring the individual laboratories’ results.
Table 2. Summary of Most Probable Values (MPV) for each parameter for each study material.
Matrix
Cocoa Powder
Tuna Fish Tissue
Certified Values
Seaweed Snack
Shellfish Tissue
White Rice Flour
Certified Values
Inorg As
(μg/kg)
19
39
11
120
110
92
MMAs
(μg/kg)
ISD
6.1
ISD
11
11
12
DMAs
(μg/kg)
ISD
140
150
140
640
180
180
AsB
(μg/kg)
ISD
4000
3896
560
1100
ISD
-
Total As
in Sample
(μg/kg)
45
4800
4800
13000
6800
310
285
Total As
in Extract
(μg/kg)
27
4400
12000
5500
320
-
ISD = insufficient data for calculation of the MPV
In order to assess the extraction efficiency of the sample preparation method used for the
speciation analyses of each sample, laboratories were asked to measure the total arsenic
concentration in both the sample and the speciation extract. The total arsenic extraction
efficiency was then calculated by dividing the MPV result for total arsenic in the extract by the
MPV result for total arsenic in the sample. Most of the participating laboratories complied with
the request and sixteen datasets were submitted with results for at least one sample for both total
As in the sample and in the speciation extract.
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The extraction efficiencies and mass balance calculations based on MPV’s for all
intercomparison samples are shown in Graph 1. The average extraction efficiency for all results
reported for the solid samples was 86%. However, the performance of the different extraction
procedures varied significantly between laboratories. The speciation mass balances in Graph 1
clearly demonstrate the need to develop additional and more effective extraction methods to be
used for diverse matrices.
Graph 1. Speciation Extraction Efficiency by Sample
103%
92%
87%
92%
97%
81%
60%
42%
28%
5%
Cocoa Powder
Tuna Fish Tissue
Seaweed Snack
Extraction Efficiency
Shellfish Tissue
White Rice Flour
Speciation Mass Balance
The majority of the laboratories that reported results for both total arsenic in the sample and total
arsenic in the extract used some form of nitric acid extraction method. Many of these laboratories
followed the procedure described by the FDA (EAM 4.11). With the exception of the highest and
the lowest values, all extraction efficiencies for samples prepared with a nitric acid extraction
method were between 75-110%. In contrast, extraction efficiencies for samples prepared with a
methanol based extraction were typically higher (89% and 94%). The two methanol extractions
were considerably different with regards to both time (1 hour and 16 hours) and temperature
(ambient and 37 oC, respectively). The extraction efficiencies were excellent and within
experimental error from each other indicating the selection of extraction solutions played a key
role in the performance of the approach. Laboratories 08 and 11 applied HCl as the extraction
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solution which yielded a similar spread of results as compared to the nitric acid approach (96%
and 129%). The extraction temperature, heating method, concentration of HCl, and inclusion of
peroxide during extraction did not have an appreciable impact on the extraction efficiency for the
two laboratories using HCl as the extraction solution which indicates, as with the methanol
extractions, the selection of extraction solutions played a key role in the performance of the
approach.
In reviewing the detailed descriptions of the sample preparation methods provided by the
laboratories, nearly all variables associated with an extraction method varied significantly.
Laboratories 05, 06, 09, 10, 12, 13, 19, 23, and 28 referenced FDA Method 4.11 as the extraction
method; however, the temperature, inclusion of peroxide, method of heating (hotblock or
microwave), and application of a buffering agent were different between most laboratories.
The MPV arsenic speciation results as a fraction of the MPV total arsenic in the samples are
shown in Graph 2. The mass balance (sum of arsenic species divided by the total arsenic results)
for the cocoa powder averaged 42% with inorganic arsenic as the predominant arsenic species.
The range of mass balance varied significantly between laboratories (26% - 97%). The average
mass balance for extractions applying nitric acid was 47% indicating the extraction solution was
incompatible with the sample matrix. The highest mass balance for the cocoa powder was
achieved by Laboratory 22 (97%); however, the extraction method was listed as “other” which
negates the possibility of correlating extraction solutions and conditions to the results.
Graph 2. Arsenic Speciation Results as a Fraction of the Total Arsenic Calculated
from the MPVs
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The overall mass balance for the tuna fish tissue was excellent (87%) throughout the
laboratories. The mass balance for eight laboratories (Laboratories 01, 02, 03, 08, 11, 16, 18, 20)
was below 10%. The low mass balances are attributed to the limited species that were reported
(total inorganic arsenic). The majority of arsenic associated with the tuna fish tissue was
arsenobetaine, which explains the low mass balances.
The seaweed snack sample resulted in the lowest mass balance out of all of the intercomparison
samples (5%). The low recoveries are attributed to the limited number of arsenic species that
were reported for calculating the mass balance (arsenite, arsenate, MMAs, DMAs, and AsB). As
part of the intercomparison study laboratories were also requested to report unidentified arsenic
species. When taking all other arsenic species into consideration the average mass balance
increases to 53% with four laboratories reporting a mass balance of greater than 90%
(Laboratories 12, 17, 22, 23). Certain sources of seaweed have been documented to contain
copious amounts of arsenosugars. When arsenosugars and unidentified arsenic species are not
taken into consideration for organisms with more complex metabolic systems low mass balances
are to be expected.
For the shellfish sample the MPV sum of species totaled 28% of the total arsenic MPV. As stated
above, the low recoveries are attributed to the limited number of arsenic species that were
reported for calculating the mass balance (arsenite, arsenate, MMAs, DMAs, and AsB). When
taking all other known arsenic species into consideration the average mass balance increases to
38%. When the additional unknown arsenic species are taken into consideration, as reported
from two laboratories, the mass balance is greater than 80% (Laboratories 17 and 22). Additional
arsenic species such as tetramethylarsonium, arsenocholine, trimethylarsine, arsenosugars, and
multiple unknown arsenic species have been documented to be present in shellfish, which the
low mass balances may be attributed to (Ref. 5).
For the white rice flour sample, the sum of the MPV arsenic species totaled 97% of the arsenic as
compared to the MPV total arsenic concentration. The white rice flour was a NIST certified
reference material and was primarily composed of carbohydrates. The simplicity of the sample
matrix makes it more amenable to higher extraction efficiencies. Few certified reference
materials are available for arsenic speciation analyses, making this CRM a likely candidate for
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laboratories offering or pursuing arsenic speciation analyses to use for the purpose of method
development and validation processes.
Discussion
Participation
A similar distribution of participating labs from North America, Europe, and other countries was
encountered as compared to the 2013 study, as can be seen in Table 4.
Of the 30 laboratories that registered to participate in this study, 29 received the study materials.
Of the 29 laboratories that received the study materials, 28 of them reported results. The list of
the participating laboratories can be found in Table 3.
Of the participating laboratories, only 6 datasets included all of the requested parameters in every
material type (laboratory numbers 04, 12, 14, 15, 17, 19, 22, and 23). Approximately 40% of the
datasets (12 of 29) did not report results for both total arsenic in the sample and total arsenic in
the extract; therefore, extraction efficiencies for those laboratories could not be calculated. All
laboratories reported at least one total arsenic value for the extract or sample.
Table 3. Participants in the 2014 Brooks Applied Labs Interlaboratory Comparison
Study for Arsenic Speciation in Food
Laboratory Name
Country
ALS Technichem (M) SDN BHD
Malaysia
Applied Speciation
USA
Brooks Rand Labs (now Brooks Applied Labs)
USA
BRUKER FRANCE
France
California Department of Public Health, Food & Drug Laboratory
USA
Canadian Food Inspection Agency (CFIA)
Canada
Cawthron Institute
New Zealand
Certified Laboratories, Inc.
USA
Dartmouth College
USA
Eurofins Central Analytical Laboratories
USA
Eurofins Frontier Global Sciences, Inc.
USA
Food and Drug Administration, Kansas City Laboratory
USA
GALAB Laboratories GmbH
Germany
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Lakehead University Environmental Laboratory
Canada
Minnesota Dept of Agriculture, Lab Services Division
USA
MSE, Inc.
USA
National Food Agency, Sweden
Sweden
National Institute of Nutrition and Seafood Research
Norway
Nestle Quality Assurance Center, Singapore
China
New York State Dept of Agriculture and Markets Food Lab
USA
OMIC USA Inc.
USA
SILLIKER JR LABORATORIES
Canada
U.S. Food & Drug Administration
USA
University of Arizona/AZ Laboratory for Emerging Contaminants
USA
US FDA - Cincinnati - Forensic Chemistry Center
USA
US FDA - San Francisco Lab
USA
Weck Labs Inc.
USA
Wisconsin Department of Agriculture, Bureau of Laboratory Services
USA
Participation in this study was international. Approximately 1/4 of the participants were from
outside of North America. Of the North American participants, 64% were from the USA, with
the remaining four laboratories from Canada. Of the laboratories from the USA, 8 (44%) were
private commercial/industry testing laboratories, 4 (22%) were state laboratories representing
five different states, 4 (22%) were laboratories associated with the FDA, and 2 (11%) were
university laboratories. There were 5 participating laboratories from Europe (17%) representing
5 different countries. In addition, there were 2 participants from Asia and 1 from Australia/New
Zealand. Table 4 summarizes the regional participation in this study and the previous study
conducted in 2013.
Table 4. Number of participating laboratories by region
Number of Participants
Number of Participants
Region
2013
2014
North America
25
64%
21
75%
Europe
8
21%
4
14%
Other
6
15%
3
11%
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Performance Ratings
In total, 368 data points were eligible for scoring. The mean scores for the different parameters
were relatively consistent, averaging 2.7 and ranging from 2.5 for the MMAs in the sample to 2.9
for the Total As in the sample, DMAs, and AsB (Table 5).
Table 5. The mean scores for each parameter for all material types.
Mean
Score
Total As in Sample 2.9
Total As in Extract
2.4
Inorganic As
2.7
MMAs
2.5
DMAs
2.9
AsB
2.9
All Parameters
2.7
Parameter
n
128
77
84
19
50
10
368
Similarly, the mean scores for the sample matrices were also relatively consistent, ranging from
2.5 for the white rice to 2.8 for the cocoa powder and tuna fish (Table 6).
Table 6. The number of laboratories receiving each score for each of the
sample matrices used in the study, along with the mean score for each matrix.
Score
Cocoa
Powder
4
3
2
1
0
Mean
9
11
3
0
3
2.8
Numbers of Labs Receiving Each Score
White
Seaweed
Rice All Matrices
Tuna Fish
Snack
Shellfish
9
8
8
2
0
2.8
11
3
6
1
2
2.7
7
9
8
1
1
2.7
7
8
8
3
1
2.5
3
18
5
2
0
2.7
Graphs 3a-3d group participating laboratories based on the performance scores for each of the
study materials. The overall scores summarized in Graph 3e.
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The fact that the majority of laboratories participating in this study (75%) achieved an overall
score of 3 or 4 (good or outstanding) indicates that, for at least some matrices, there is generally
good intercomparability amongst most laboratories that reported total arsenic and arsenic
speciation data for these matrices. 93% of the laboratories received an overall score of 2 or
better, and only 2 laboratories (7%) received scores of 1 or 0 (poor or unacceptable,
respectively). However, with only 3 laboratories (11%) receiving an overall score of 3.5 or
higher, further analytical method development is required in order to achieve a high level of
consistency across multiple laboratories using various methods worldwide.
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When reviewing this report, keep in mind that the study materials do not have “true” or
“assigned” values; with the exception of the white rice and tuna fish. The MPVs were
determined based on the median of the results. Therefore, if many laboratories used the same
method, and that method is prone to species conversion or species co-elution, then the resulting
MPVs have the risk of being biased. For example, many laboratories used a nitric acid sample
extraction for the speciation analyses, which has the potential to cause oxidation of some or all of
the As(III) to As(V). In addition, when extracts of samples containing significant levels of AsB
(e.g., sea plants or seafood) are analyzed on some column types, co-elution of As(III) and these
large organic arsenic molecules is a risk if steps aren’t taken to mitigate these interferences. The
issue is further exacerbated by the co-elution of tetramethylarsonium, arsenocholine, and
trimethylarsine. It has also been documented that application of nitric acid, especially in the
presence of peroxide, has a high capacity for degrading certain arsenosugars to DMAs (Ref. 6).
Of course, certain organisms such as shellfish, algae, seaweed, and other more esoteric substrates
can contain unknown arsenic species which can also degrade or co-elute with known arsenic
species. Please refer to Table 7 for a summary of the inorganic As, AsB, and unknown arsenic
species results reported for the seaweed sample, along with the associated high performance
liquid chromatography (HPLC) column type. The laboratory identification numbers have been
altered to preserve confidentiality regarding methodology. The inorganic As, AsB, and DMAs
results reported for the seaweed sample were so variable, the results could not be scored (F value
greater than M value). The specific column type did not correlate with the any of the reported
arsenic speciation results.
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Table 7. Subset of Seaweed Snack Data Demonstrating the Variability in Inorganic As,
DMAs, Unknown Arsenic, and AsB as Correlated to HPLC column Type.
Lab ID
A
B
C
D
E
F
G
H
I
J
K
L
M
N
O
P
Q
Inorganic As
DMAs
AsB
Unidentified
As species
not reported
445
not reported
not reported
not reported
56
not reported
not reported
not reported not reported
not reported
330
not reported
27
not reported
8262
not reported not reported
36
not reported not reported
7482
not reported
not reported
not reported
136
10861
not reported
not reported
44
35
8190
not reported
710
8100
not reported
11
not reported
25
13760
20
2250
not reported
not reported
not reported
1020
560
14600
18
not reported not reported
not reported
21
63
not reported
12400
462
1037
10419
not reported
6612
not reported not reported
not reported
10600
662
not reported
not reported
Column Type
Hamilton PRP-x100
Hamilton PRP-x100
not reported
Dionex AS7
Dionex AS7
not reported
Hamilton PRP-x100
Hamilton PRP-x100
Hamilton PRP-x100
Agilent G3288-80000
not reported
Hamilton PRP-x100
not reported
not reported
Hamilton PRP-x100
not reported
Hamilton PRP-x100
Methods and Equipment Used
For the analysis of total As, the majority of participating laboratories used microwave digestion
and ICP-MS analysis with an Agilent instrument. Refer to Table 8 for details of the sample
preparation and analysis methods used to determine the total As.
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Table 8. Sample Preparation and Analysis Methods, and Analytical
Instrumentation, Used for the Analysis of Total As.
Total As Sample Preparation Method
No. of Labs
Microwave Digestion
22
76%
Hotblock/Hotplate Digestion
None or Other
6
1
21%
3%
Total As Analysis Method
ICP-MS
No. of Labs
29
100%
Total As Instrument Manufacturer
Agilent
Perkin Elmer
Thermo
Bruker
Varian
Not Listed
No. of Labs
13
45%
8
28%
3
10%
1
3%
1
3%
3
10%
For the speciation of arsenic, the majority of participating laboratories used a nitric acid
extraction, HPLC separation, and ICP-MS analysis with an Agilent instrument. Refer to Table 9
for details of the sample preparation, separation, and detection methods used in this study.
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Table 9. Sample preparation separation, and detection methods, and analytical instrumentation,
used for the analysis of As speciation.
As Speciation Sample Preparation Method
HNO3 Extraction
No. of Labs
18
64%
Other
Enzyme Extraction
3
1
11%
4%
HCl Extraction
4
14%
Methanol Extraction
2
7%
As Speciation Separation Method
HPLC
Other/Not Defined
HG-CT-GC
No. of Labs
23
82%
3
11%
2
7%
As Speciation Detection Method
ICP-MS
HG-AAS
Other/Not Defined
No. of Labs
25
89%
2
7%
1
4%
As Speciation Instrument Manufacturer
Agilent
Perkin Elmer
Bruker
Buck
Other/Not Defined
No. of Labs
15
54%
8
29%
1
4%
1
4%
3
11%
Future Studies
This year’s study utilized five common food types with very diverse matrices. The consistency
that was seen with the white rice and the extensive variability observed with some of the other
matrix types indicate that different extractions and methodologies may be appropriate to
determine the various arsenic species specific to the matrix type.
As the differing technologies for arsenic speciation become more common and more widely
practiced, there are even more compelling reasons to continue this study and it is hoped that in
increased participation will be seen in future studies.
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Brooks Applied Labs hopes to continue conducting this study in the future. Any feedback on the
2014 study or interest in participating in future studies should be directed to Elizabeth Madonick
([email protected]).
The purpose of this report is to summarize the study results without detailed interpretation of the
data. Discussion regarding the chemistry of the different arsenic species, arsenic species not
included in this study, and the vast array of different sample matrices that are available is beyond
the scope of this report. It is with sincere hope that each participating laboratory and other
laboratories offering or pursuing arsenic speciation analyses in tissue matrices continue their
research, method development, and method validation. Without harmonized methods, as
supported by the findings of this intercomparison study, results can vary significantly between
laboratories and technologies.
Acknowledgements
This study was made possible by the dedicated effort and input of many people. Michela
Hernandez at EcoChem, Inc. received, organized, anonymized, and archived all of the data. The
format of this study was based on the report for the outstanding Brooks Rand Instruments
Interlaboratory Comparison Study for Total Mercury and Methylmercury, authored by Joel
Creswell, Virginia Engel, Annie Carter, and Colin Davies (Ref. 7).
Many members of the Brooks Applied Labs staff contributed to the success of this project.
Samantha Dillon and Scott Anderson, and assisted with assembling and shipping of the kits of
study materials. Margaret Shultz coordinated the distribution of information and corresponded
with participant as shipping issues arose. Tamas Ugrai, Abigail Rudd, Ian Joslin, and Christabel
Escarez performed the screening analyses of several batches containing prospective products to
ensure total arsenic concentrations were suitable for this study.
The participants were all asked to pay a small fee for participation to cover shipping costs. Bill
Dewey of Taylor Shellfish generously donated enough geoducks to serve as one of the materials
for this study. Laura Wood of NIST donated the NIST white rice flour certified reference
material to be used in the study. Perkin Elmer and Agilent Technologies supported this study
with funding to cover a portion of the costs associated with obtaining and prescreening materials
for the study as well as the materials and assembly required to build the study kits for the
20 of 39
participants. The remaining funding associated with producing this intercomparison study and
the associated report was provided by Brooks Applied Labs.
References
1) Helsel, D.R. (2009) Summing Nondetects: Incorporating Low-Level Contaminants in
Risk Assessment, Integrated Environmental Assessment and Management, volume 6,
number 3, pp 361-366.
2) R version 3.1.2 (2014-10-31), The R Foundation for Statistical Computing Platform
(2014).
3) United States Geological Society’s Standard Reference Sample Project, Office of Water
Quality, Branch of Quality Systems. http://bqs.usgs.gov/srs/SRS_Spr04/statrate.htm
4) Hoaglin, D.C., Mosteller, F. and Tukey, J.W. (eds.) (1993) Understanding Robust and
Exploratory Data Analysis, Wiley, New York, NY.
5) Larsen, E., Quetal, C., Munoz, R., Fiala-Medioni, A., Donard, O. (1997) Arsenic
speciation in shrimp and mussels from the Mid-Atlantic hydrothermal vents, Marine
Chemistry, volume 57, pp 341-346.
6) Bluemlein, K., Raab, A., Meharg, A., Charnock, J., Feldmann, J. Can we trust mass
spectrometry for determination of arsenic peptides in plants: comparison of LC–ICP–MS
and LC–ES-MS/ICP–MS with XANES/EXAFS in analysis of Thunbergia alata, Analytical
and Bioanalytical Chemistry, volume 390, pp 1739-1751.
7) Creswell, J., Engel, V., Carter, A., and Davies, C. (2013) 2013 Brooks Rand Instruments
Interlaboratory Comparison Study for Total Mercury and Methylmercury (Intercomp
2013). Brooks Rand Instruments, Seattle, WA.
21 of 39
Table A1. Total As Results for Cocoa Powder and Tuna Fish
Sample 1 - Cocoa Powder
Total As in Sample
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
39.4
56.5
< 50
44.0
40.5
45.0
42.1
109.0
39.4
62.0
45.0
39.8
55.0
49.8
128.0
36.5
34.8
48.5
48.5
37.0
42.0
19.4
54.9
70.0
79.8
not measured
not measured
49.0
Median (M) =
Mean =
F-psuedosigma (F) =
n=
MPV =
Z-Value
Rating
0.50
1.02
0.09
0.40
0.00
0.26
5.68
0.50
1.50
0.00
0.47
0.88
0.42
7.23
0.76
0.91
0.31
0.31
0.71
0.27
2.28
0.87
2.21
3.08
0.35
45.0
52.6
11.3
25
4
2
4
4
4
4
0
4
2
4
4
3
4
0
3
3
4
4
3
4
0
3
0
0
4
μg/kg
μg/kg
45
μg/kg
Sample 2 - Tuna Fish Tissue
Total As in Sample
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
4400
5458
4250
4650
4550
5093
4367
4930
4635
6028
4600
3961
5080
4340
4140
5075
4880
5410
5410
4317
5810
4240
4806
5525
5476
not measured
4680
5183
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Sample Source Material:
Certified Value =
Uncertainty =
MPV =
Z-Value
Rating
0.60
3
0.96
3
0.82
3
0.23
4
0.38
4
0.42
4
0.65
3
0.18
4
0.25
4
1.81
1
0.30
4
1.25
2
0.40
4
0.69
3
0.98
3
0.40
4
0.11
4
0.89
3
0.89
3
0.72
3
1.48
2
0.84
3
0.00
4
1.06
2
0.99
3
0.19
4
0.56
3
4806
μg/kg
4863
μg/kg
677
27
IRMM BCR-627
4800
μg/kg
300
μg/kg
4800
μg/kg
22 of 39
Table A2. Total As Results for Seaweed and Shellfish
Sample 3 - Seasoned Seaweed Snack
Total As in Sample
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
Z-Value
Rating
12700
11597
13780
12350
12700
13178
12237
15900
13887
1499
13000
11539
15200
12000
11000
12194
14300
17700
17700
12865
not measured
12600
13058
16050
18167
not measured
14700
15475
Median (M) =
Mean =
F-psuedosigma (F) =
n=
0.16
0.69
0.36
0.33
0.16
0.07
0.38
1.38
0.41
5.54
0.01
0.72
1.04
0.49
0.97
0.40
0.61
2.24
2.24
0.08
0.21
0.01
1.45
2.47
0.80
1.17
13029
13361
2083
26
4
3
4
4
4
4
4
2
4
0
4
3
2
4
3
4
3
0
0
4
4
4
2
0
3
2
μg/kg
μg/kg
MPV =
13000
μg/kg
Sample 4 -Shellfish Tissue
Total As in Sample
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
Z-Value
Rating
6180
6370
6390
6905
6260
6719
6220
7400
7198
8218
6800
5876
7400
6560
6070
6992
5840
7220
7220
6497
not measured
6290
6819
6940
7486
not measured
6840
7493
Median (M) =
Mean =
F-psuedosigma (F) =
n=
0.94
0.66
0.63
0.14
0.82
0.14
0.88
0.88
0.58
2.10
0.01
1.39
0.88
0.37
1.10
0.27
1.45
0.61
0.61
0.47
0.77
0.01
0.19
1.01
0.05
1.02
6810
6777
670
26
3
3
3
4
3
4
3
3
3
0
4
2
3
4
2
4
2
3
3
4
3
4
4
3
4
2
μg/kg
μg/kg
MPV =
6800
μg/kg
23 of 39
Table A3. Total As Result
Sample 5 - White Rice Flour
Total As in Sample
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
298
342
270
311
320
358
282
322
318
361
290
259
325
262
265
305
315
313
313
290
301
262
296
371
442
285
not measured
319
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Sample Source Material:
Certified Value =
Uncertainty =
MPV =
Z-Value
Rating
0.52
3
1.23
2
1.65
1
0.00
4
0.36
4
1.88
1
1.18
2
0.44
4
0.27
4
2.01
1
0.85
3
2.09
0
0.56
3
1.97
1
1.85
1
0.23
4
0.16
4
0.08
4
0.08
4
0.85
3
0.40
4
1.97
1
0.60
3
2.42
0
5.40
0
1.05
2
0.32
4
311
μg/kg
311
μg/kg
25
27
NIST 1568b
285
μg/kg
14
μg/kg
310
μg/kg
24 of 39
Table A4. Total As Results for Cocoa Powder and Tuna Fish Speciation Extracts
Sample 1 - Cocoa Powder
Sample 2 - Tuna Fish Tissue
Total As in Extract
Total As in Extract
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
not measured
52.7
not measured
17.0
not measured
not measured
not measured
100.0
not measured
not measured
35.0
1.62*
not measured
38.5
49.2
17.6
27.2
< 160
20.0
not measured
27.0
17.7
57.1
not measured
not measured
not measured
not measured
31.0
Median (M) =
Mean =
F-psuedosigma (F) =
n=
MPV =
Z-Value
1.00
0.65
4.40
0.18
1.70
0.35
0.84
0.62
0.18
0.51
0.18
0.62
1.21
0.00
31.0
37.7
21.6
13
27
Rating
3
3
0
4
1
4
3
3
4
4
4
3
2
4
μg/kg
μg/kg
μg/kg
*Value omitted from statistics (see narrative)
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
not measured
4797
not measured
4281
not measured
not measured
not measured
4780
not measured
not measured
7000
231*
not measured
4490
4430
4255
4690
4120
4770
not measured
4190
4337
4984
not measured
not measured
not measured
5000
4002
Median (M) =
Mean =
F-psuedosigma (F) =
n=
MPV =
Z-Value
0.80
0.54
0.75
6.51
11.04
0.00
0.16
0.61
0.52
0.96
0.73
0.78
0.40
1.28
1.32
1.27
4490
4675
386
15
4400
Rating
3
3
3
0
0
4
4
3
3
3
3
3
4
2
2
2
μg/kg
μg/kg
μg/kg
*Value omitted from statistics (see narrative)
25 of 39
Table A5. Total As Results for Seaweed and Shellfish Speciation Extracts
Sample 3 - Seasoned Seaweed Snack
Sample 4 -Shellfish Tissue
Total As in Extract
Total As in Extract
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
Z-Value
not measured
11607
not measured
8389
not measured
not measured
not measured
11300
not measured
not measured
16100
686*
not measured
10000
10700
10878
13800
12000
16300
not measured
not measured
13300
12737
not measured
not measured
not measured
10000
13025
Median (M) =
Mean =
F-psuedosigma (F) =
n=
MPV =
0.11
1.85
0.27
2.33
6.03
0.98
0.60
0.50
1.08
0.11
2.44
0.81
0.51
0.98
0.66
11803
12153
1843
14
12000
Rating
4
1
4
0
0
3
3
4
2
4
0
3
4
3
3
μg/kg
μg/kg
μg/kg
*Value omitted from statistics (see narrative)
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
not measured
5574
not measured
3064
not measured
not measured
not measured
7010
not measured
not measured
9400
281*
not measured
4840
6050
5119
5620
5510
5940
not measured
not measured
5450
5363
not measured
not measured
not measured
7200
5408
Median (M) =
Mean =
F-psuedosigma (F) =
n=
MPV =
Z-Value
0.07
5.16
3.06
8.03
10.95
1.46
1.06
0.88
0.16
0.07
0.83
0.19
0.37
3.45
0.28
5542
5825
481
14
5500
Rating
4
0
0
0
0
2
2
3
4
4
3
4
4
0
4
μg/kg
μg/kg
μg/kg
*Value omitted from statistics (see narrative)
26 of 39
Table A6. Total As Result for Rice Speciation Exrtacts
Sample 5 - White Rice Flour
Total As in Extract
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
not measured
366
not measured
312
not measured
307
333
400
not measured
271
450
19*
not measured
341
556
316
243
310
320
not measured
321
288
343
303
not measured
not measured
not measured
288
Median (M) =
Mean =
F-psuedosigma (F) =
n=
MPV =
Z-Value
1.69
0.21
0.39
0.53
2.89
1.67
4.65
10.54
0.81
8.38
0.07
2.64
0.28
0.07
0.10
1.06
0.87
0.53
1.06
318
337
28
18
320
Rating
1
4
4
3
0
1
0
0
3
0
4
0
4
4
4
2
3
3
2
μg/kg
μg/kg
μg/kg
*Value omitted from statistics (see narrative)
27 of 39
Table A7. Inorganic Arsenic Results for Cocoa Powder and Tuna Fish
Sample 1 - Cocoa Powder
Sample 2 - Tuna Fish Tissue
Inorganic As
Inorganic As
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
20.2
19.8
27.0
17.0
not measured
not measured
< 40
29.0
not measured
not measured
17.0
18.4
not measured
16.4
19.2
17.6
11.4
28.0
19.0
25.8
26.0
18.9
21.2
not measured
< 39.4
not measured
not measured
22.0
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
0.14
0.05
1.44
0.48
1.83
0.48
0.21
0.59
0.05
0.35
1.55
1.64
0.09
1.21
1.25
0.12
0.33
0.48
19.5
20.8
5.2
18
Rating
4
4
2
4
1
4
4
3
4
4
1
1
4
2
2
4
4
4
μg/kg
μg/kg
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
12.0
35.7
150.0
49.0
not measured
not measured
94.3
36.0
not measured
not measured
80.0
15.4
not measured
55.2
< 3.5 FN
< 5 FN
72.0
36.0
36.0
88.0
100.0
38.8
58.9
not measured
1998.0
not measured
< 7 FN
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
Rating
1.12
0.51
2.46
0.16
1.01
0.50
0.64
1.03
0.00
0.44
0.50
0.50
0.85
1.16
0.43
0.09
57.07
55.2
173.8
38.5
17
2
4
0
4
2
4
3
2
4
0
0
4
4
4
3
2
4
4
0
0
μg/kg
μg/kg
39
μg/kg
FN = False Negative
MPV =
19
μg/kg
MPV =
28 of 39
Table A8. Inorganic Arsenic Results for Seaweed and Shellfish
Sample 3 - Seasoned Seaweed Snack
Inorganic As
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
< 5.31
< 7.49
330
< 10
not measured
not measured
8262
36
not measured
not measured
<4
< 0.105
not measured
< 20
< 3.5
<5
11
20
< 114
18
not measured
21
462
not measured
6612
not measured
<7
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
36
1753
328
9
Data too variable to use MPV for scoring
MPV =
11
Rating
μg/kg
μg/kg
Sample 4 -Shellfish Tissue
Inorganic As
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
29
117
250
21
not measured
not measured
280
134
not measured
not measured
140
61
not measured
39
< 3.5 FN
93
38
120
141
158
not measured
135
117
not measured
2001
not measured
200
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
Rating
1.56
0.16
1.96
1.69
2.43
0.11
0.21
1.05
1.41
0.54
1.41
0.11
0.22
0.49
0.14
0.16
31.72
1.16
127
226
63
18
1
4
1
1
0
4
4
2
2
0
3
2
4
4
4
4
4
0
2
μg/kg
μg/kg
120
μg/kg
FN = False Negative
μg/kg
MPV =
29 of 39
Table A9. Inorganic Arsenic Results for Rice
Sample 5 - White Rice Flour
Inorganic As
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
112
67
90
117
118
124
99
125
110
106
130
98
76
82
103
120
70
105
95
147
97
108
107
92
165
109
not measured
102
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Sample Source Material:
Certified Value =
Uncertainty =
MPV =
Z-Value
Rating
0.40
4
2.42
0
0.99
3
0.71
3
0.77
3
1.12
2
0.45
4
1.21
2
0.29
4
0.00
4
1.52
1
0.48
4
1.89
1
1.48
2
0.17
4
0.88
3
2.26
0
0.04
4
0.67
3
2.59
0
0.55
3
0.15
4
0.10
4
0.86
3
3.72
0
0.21
4
0.21
4
106
μg/kg
106
μg/kg
16
27
NIST 1568b
92
μg/kg
10
μg/kg
110
μg/kg
30 of 39
Table A10. Dimethylarsinic Acid Results for Cocoa Powder and Tuna Fish
Sample 1 - Cocoa Powder
Sample 2 - Tuna Fish Tissue
DMAs
DMAs
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
< 5.31
1.14
not measured
<2
not measured
not measured
< 20
not measured
not measured
not measured
not measured
1.05
not measured
1.26
< 1.4
<5
< 10
< 12
<3
not measured
2.00
< 2.2
< 6.22
not measured
not measured
not measured
not measured
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
1.20
1.36
0.24
4
Insufficient datapoints to calculate MPV
Rating
μg/kg
μg/kg
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
158
129
not measured
138
not measured
not measured
131
not measured
not measured
not measured
not measured
101
not measured
145
80
234
105
127
251
not measured
200
214
161
not measured
not measured
not measured
< 3.47 FN
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Sample Source Material:
Certified Value =
Uncertainty =
MPV =
Z-Value
Rating
0.36
4
0.26
4
0.08
4
0.22
4
0.87
3
0.08
4
1.33
2
1.99
1
0.79
3
0.31
4
2.36
0
1.26
2
1.56
1
0.42
4
0
142
μg/kg
155
μg/kg
46
14
IRMM BCR-627
149.8
μg/kg
22.5
μg/kg
140
μg/kg
31 of 39
Table A11. Dimethylarsinic Acid Results for Seaweed and Shellfish
Sample 3 - Seasoned Seaweed Snack
DMAs
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
445
56
not measured
27
not measured
not measured
not measured
not measured
not measured
not measured
not measured
136
not measured
44
710
<5
< 10
2250
1020
not measured
not measured
63
1037
not measured
not measured
not measured
10600
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
445
1490
718
11
Data too variable to use M for scoring
MPV =
140
Rating
μg/kg
μg/kg
μg/kg
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Sample 4 -Shellfish Tissue
DMAs
Result (μg/kg)
Z-Value
Rating
not measured
385
not measured
391
not measured
not measured
422
not measured
not measured
not measured
not measured
355
not measured
425
1340
672
284
1030
1080
not measured
not measured
644
1136
not measured
not measured
not measured
2880
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
0.51
0.50
0.43
0.57
0.43
1.36
0.06
0.70
0.76
0.85
0.00
0.96
4.85
644
850
511
13
4
4
4
3
4
2
4
3
3
3
4
3
0
μg/kg
μg/kg
MPV =
640
μg/kg
32 of 39
Table A12. Dimethylarsinic Acid Results for Rice
Sample 5 - White Rice Flour
DMAs
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
170
142
not measured
182
181
166
148
not measured
170
154
not measured
182
181
141
149
183
157
136
205
not measured
180
177
183
197
not measured
182
not measured
184
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Sample Source Material:
Certified Value =
Uncertainty =
MPV =
Z-Value
Rating
0.43
4
1.81
1
0.16
4
0.11
4
0.62
3
1.51
2
0.41
4
1.22
2
0.16
4
0.11
4
1.86
1
1.46
2
0.21
4
1.07
2
2.10
0
1.30
2
0.07
4
0.07
4
0.22
4
0.90
3
0.16
4
0.28
4
179
μg/kg
171
μg/kg
20
22
NIST 1568b
180
μg/kg
12
μg/kg
180
μg/kg
33 of 39
Table A13. Monomethylarsonic Acid Results for Cocoa Powder and Tuna Fish
Sample 1 - Cocoa Powder
Sample 2 - Tuna Fish Tissue
MMAs
MMAs
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
< 5.31
< 0.337
not measured
<2
not measured
not measured
< 20
not measured
not measured
not measured
not measured
0.46
not measured
< 0.982
< 1.8
<5
< 10
<9
<2
not measured
0.70
< 3.89
< 6.51
not measured
not measured
not measured
not measured
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
0.58
0.58
0.09
2
Rating
μg/kg
μg/kg
Insufficient datapoints to calculate MPV
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
< 5.31
9
not measured
41
not measured
not measured
< 20
not measured
not measured
not measured
not measured
8
not measured
6
< 2.5
<5
16
< 20
< 14
not measured
1
8
39
not measured
not measured
not measured
< 3.47
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
8.8
16.0
10.1
8
Data too variable to use M for scoring
MPV =
6.1
Rating
μg/kg
μg/kg
μg/kg
34 of 39
Table A13. Monomethylarsonic Acid Results for Seaweed and Shellfish
Sample 3 - Seasoned Seaweed Snack
Sample 4 -Shellfish Tissue
MMAs
MMAs
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
< 5.31
< 3.37
not measured
not measured
not measured
not measured
822
not measured
not measured
not measured
not measured
< 0.067
not measured
< 13
< 1.8
<5
< 10
< 321
< 57
not measured
not measured
< 4.83
418
not measured
not measured
not measured
< 3.47
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
620
620
150
2
Rating
μg/kg
μg/kg
Insufficient datapoints to calculate MPV
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
< 5.31
11
not measured
not measured
not measured
not measured
951
not measured
not measured
not measured
not measured
65
not measured
11
< 1.8
<5
62
< 95
< 25
not measured
not measured
19
78
not measured
not measured
not measured
< 3.49
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
MPV =
Z-Value
Rating
1.22
21.40
0.07
1.23
0.00
1.02
0.39
62
171
42
7
2
0
4
2
4
2
4
μg/kg
μg/kg
11
μg/kg
35 of 39
Table A14. Monomethylarsonic Acid Results for Rice
Sample 5 - White Rice Flour
MMAs
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
< 5.31 FN
10.0
not measured
13.0
14.0
17.2
< 20
not measured
11.4
11.1
not measured
11.8
15.3
10.2
< 1.8 FN
13.4
15.2
< 18
13.0
not measured
8.0
10.6
40.5
14.0
not measured
12.1
not measured
13.7
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Sample Source Material:
Certified Value =
Uncertainty =
FN = False Negative
MPV =
Z-Value
Rating
0
1.46
2
0.00
4
0.48
4
2.04
0
0.77
3
0.90
3
0.58
3
1.11
2
1.35
2
0
0.19
4
1.06
2
0.00
4
2.41
0
1.17
2
13.25
0
0.48
4
0.43
4
0.34
4
13.0
μg/kg
14.1
μg/kg
2.1
18
NIST 1568b
11.6
μg/kg
3.5
μg/kg
11
μg/kg
36 of 39
Table A15. Arsenobetaine Results for Cocoa Powder and Tuna Fish
Sample 1 - Cocoa Powder
AsB
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
not measured
not measured
not measured
<2
not measured
not measured
< 20
not measured
not measured
not measured
not measured
< 0.051
not measured
< 0.407
14
not measured
< 10
not measured
<2
not measured
not measured
< 3.9
< 3.37
not measured
not measured
not measured
not measured
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
N/C
N/C
N/C
1
Rating
μg/kg
μg/kg
Insufficient datapoints to calculate MPV
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Sample 2 - Tuna Fish Tissue
AsB
Result (μg/kg)
not measured
not measured
not measured
3954
not measured
not measured
3996
not measured
not measured
not measured
not measured
4165
not measured
3550
3590
not measured
3650
not measured
4750
not measured
3730
not measured
4644
not measured
not measured
not measured
5770
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Sample Source Material:
Certified Value =
Uncertainty =
MPV =
Z-Value
Rating
0.03
4
0.03
4
0.30
4
0.67
3
0.61
3
0.51
3
1.22
2
0.39
4
1.06
2
2.83
0
3975
μg/kg
4180
μg/kg
633
10
IRMM BCR-627
3896
μg/kg
225
μg/kg
4000
μg/kg
37 of 39
Table A16. Arsenobetaine Results for Seaweed and Shellfish
Sample 3 - Seasoned Seaweed Snack
AsB
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
not measured
not measured
not measured
< 10
not measured
not measured
not measured
not measured
not measured
not measured
not measured
10861
not measured
35
8100
not measured
25
not measured
560
not measured
not measured
not measured
10419
not measured
not measured
not measured
662
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
662
4380
6643
7
Data too variable to use M for scoring
MPV =
560
Rating
μg/kg
μg/kg
μg/kg
Sample 4 -Shellfish Tissue
AsB
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
not measured
not measured
not measured
765
not measured
not measured
not measured
not measured
not measured
not measured
not measured
3330
not measured
770
2980
not measured
1080
not measured
920
not measured
not measured
not measured
3571
not measured
not measured
not measured
1470
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
1275
1861
1620
8
Data too variable to use M for scoring
MPV =
1100
Rating
μg/kg
μg/kg
μg/kg
38 of 39
Table A17. Arsenobetaine Results for Rice
Sample 5 - White Rice Flour
AsB
Lab ID
01
02
03
04
05
06
07
08
09
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
29
Result (μg/kg)
not measured
not measured
not measured
<2
not measured
not measured
< 20
not measured
not measured
not measured
not measured
< 0.051
not measured
< 0.407
18
not measured
< 10
not measured
<2
not measured
not measured
< 7.2
< 3.37
not measured
not measured
not measured
not measured
not measured
Median (M) =
Mean =
F-psuedosigma (F) =
n=
Z-Value
N/C
N/C
N/C
1
Rating
μg/kg
μg/kg
Insufficient datapoints to calculate MPV
39 of 39